Aquatic Invertebrates in Pool and Riffle Habitats of Blackburn Fork - PowerPoint PPT Presentation

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Aquatic Invertebrates in Pool and Riffle Habitats of Blackburn Fork

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Title: Aquatic Invertebrates in Pool and Riffle Habitats of Blackburn Fork


1
Aquatic Invertebrates in Pool and Riffle Habitats
of Blackburn Fork
  • Michael Railling
  • Wildlife and Fisheries Science
  • Tennessee Tech

2
Project summary
  • Problem Are the aquatic invertebrates the same
    in pool and riffle habitats.
  • Objective Show that the two habitats should be
    comparably different by scoring the different
    taxa.
  • Expected Results In the pool more tolerant taxa
    will be found. The Riffle will support taxa that
    are more susceptible to poor water quality.

3
Introduction/Background
  • Stream macroinvertebrate assemblage varies at
    both regional and local scales (Heino et al.
    2002). My experiment the samples are taken only
    feet away from each other, however the Taxa
    Richness and Percent EPTs should be different.
  • Lower water quality is directly associated to
    diversity (Heino et al. 2002). The water quality
    of pool areas is lower than that of Riffles
    causing less diversity.

4
Objective/Hypothesis Statement
  • Hypothesis
  • What different proportions of Genera can be
    found in pool and riffle habitats of the
    Blackburn Fork, and can the differences of genera
    be linked to different water quality within
    theses habitatats.
  • Objective
  • To show that different genera are found in
    different habitats. Using Taxa Richness and
    Percent EPTs

5
Methods
  • Using 6 Hester-Dendy samplers Qualitatively, 3 in
    pools and 3 in riffles.
  • Scrubbing the bugs off the substrate
  • Identifying the invertebrates down to genus.
  • Scoring the results using data forms to show the
    Taxa Richness and Percent EPTs (State of
    Tennessee 2002).

6
Materials
  • Six Hester-Dendy Samplers with nine three inch
    plates on each.
  • One pint Formalin
  • One pint Ethyl alcohol
  • One D-Frame net
  • 12 bricks
  • One case of viles
  • One large cooler
  • 24 freezer bags

7
Expected Results and Benefits
  • Expected Results In the pool more tolerant taxa
    will be found. The Riffle will support taxa that
    are more susceptible to poor water quality such
    as EPTs.
  • Benefits Showing that invertebrates are habitat
    specific.

8
Project Timeline
  • Title 8/20/03-9/03/03
  • Objective 9/10/03-9/17/03
  • Literature References 9/17/03-present
  • Data Form 9/24/03-present
  • Experiment 8/9/03-present

9
Literature Cited
  • Adams, S.M., W.R. Hill, M.J. Peterson, M. G.
    Ryon, J. G. Smith, and A.J. Stewart. 2002.
    Assessing recovery in a stream ecosystem
    Applying chemical and biological endpoints.
    Ecological Applications 12 1510-1527.
  • Battin, T.J., L.A. Kaplan, J.D. Newbold, and
    Susan Hendricks. 2003. A mixing model of stream
    solute dynamics and the contribution of a
    hyporheic zone to ecosystem function. Freshwater
    Biology 48 995- 1014.
  • Carter, J.L., and V.H. Resh. 2001. After site
    selection and before data analysis Sampling,
    sorting, and labratory procedures used in stream
    benthic macroinvertebrates monitoring programs by
    USA state agencies. Journal of the North American
    Benthological Society 20 658-682.
  • Dyer, S.D. and Xinhao Wang. 2002 A comparison of
    stream biological responses to discharge from
    wastewater treatment plants in high and low
    population density areas. Environmental
    Toxicology and Chemistry 21 1065-1075.
  • Fairchild, M.P., and Joseph P. Holomuzki. 2002.
    Spatial variability and assemblage structure of
    stream hydrosychid caddisflies. Journal of the
    North American Benthological Society 21 576-590.
  • Heino, J., T. Muotka, and R. Paavola. 2003.
    Determinates of macroinvertebrate diversity in
    headwater streams Regional and local influences.
    2003. Journal of Animal Ecology 72 425-434.
  • Hoffman, A., and V.W. Resh. Oviposition in three
    species of limnephiloid caddisflies(Trichoptera)
    Hierarchical influences on site selection. 2003.
    Freshwater Biology 481064-1077.
  • Hyne, R.V., and W.A. Maher. Invertebrate
    biomarkers Links to toxicosis that predict
    population decline. 2003. Ecotoxicology and
    Environmental Safety 54366-374.
  • Kobayashi, S., and T. Kagaya. 2002. Differences
    in litter characteristics and macroinvertebrate
    assemblages between litter patches in pools and
    riffles in headwater stream. Limnology 337-42.
  • Malmqvist, B. 2002. Aquatic invertebrates in
    riverine landscapes. Freshwater Biology
    47679-694.
  • Negishi, J.N., M. Inoue, and M. Nunokawa. 2002.
    Effects of channelisation on stream habitat in
    relation to a spate and flow refugia for
    macroinvertebrates in northern Japan. 2002.
    Freshwater Biology 471515-1529.
  • Parsons, M., M.C. Thoms, and R.H. Norris. 2003.
    Scales of macroinvertebrate distribution in
    relation to the hierarchical organization of
    river systems. Journal of the Americam
    Benthological Society 22 105-122.
  • State of Tennessee. 2002. Quality System Standard
    Operating Procedure for Macroinvertebrate Stream
    Surveys. Department of Environment and
    Conservation.
  • Wymer, W.A., and S.B. Cook. 2003. Effects of
    Chironomidae (Diptera) taxanomic resolution on
    multivariate analysis of aquatic insect
    communities. Journal of Freshwater Ecology
    18179-186.

10
Budget
  • Saleries and Wages
    Year 1 Year 2
  • Professional
    150.00 150.00
  • Technician
    65.00 65.00
  • Secretarial
    90.00 90.00
  • Subtotal
    305.00 305.00
  • Benefits
    - -
  • Travel
    25.00 25.00
  • Non- Expendables
    100.00 100.00
  • Expendables
  • Computer
    700.00 -
  • Supplies and Expenses
    278.13 6.94
  • Copying and Telephone
    20.00 20.00
  • Subtotal
    998.13 26.94
  • Indirect Cost
    125.00 125.00
  • Direct Cost
    1303.13 331.94
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